Overcoming Trifluralin Antagonism of Glyphosate

Total Page:16

File Type:pdf, Size:1020Kb

Overcoming Trifluralin Antagonism of Glyphosate Eleventh Australian Weeds Conference Proceedings OVERCOMING TRIFLURALIN ANTAGONISM OF GLYPHOSATE Wendy Bedggood Daratech Pty. Ltd., Victorian Institute for Dryland Agriculture, Private Bag 260, Horsham, Victoria 3400, Australia Summary Investigations into the cause of loss of A series of experiments were conducted to isolate the glyphosate activity were carried out after reports of factors effecting antagonism and to find a means of over- reduced glyphosate activity in trifluralin glyphosate tank coming trifluralin antagonism of glyphosate. mixes used in the 1995 cropping season. It was found that the antagonism increases as the ratio of trifluralin to MATERIALS AND METHODS glyphosate increases and at a ratio of 2:1 significant loss A series of bioassays was conducted to compare the phy- of glyphosate activity occurred. The antagonism was totoxicity of various tank mixes of trifluralin and eliminated by the addition of ammonium sulphate at 2% glyphosate. First an experiment assessed the effect of of spray solution. three ratios of trifluralin to glyphosate on activity of glyphosate. A second experiment assessed four spray ad- INTRODUCTION ditives for their ability to reduce antagonism. A final In the 1995 cropping season wet weather delayed the bioassay verified the results with dose response curves to sowing of winter crops and limited paddock preparation measure the reduction of antagonism by ammonium sul- time. As a result there was insufficient time to apply pre- phate. and post-emergent herbicides in separate operations. Consequently an off label tank mix of trifluralin and Plants Oats (Avena sativa L. cv. Echidna) were grown in glyphosate was used widely in the Wimmera. Some her- Debco® potting mix and supplied with adequate nutri- bicide sales representatives estimated that 30% of the ents (1 plant per 10 cm diameter pot). Plants were grown trifluralin sold in the Wimmera last year was used in this in the glasshouse until they reached the 1.5 to 2-leaf stage tank mix. Most farmers were satisfied with the results (14 days). Uniform plants, one plant per replicate, were from this tank mix, however there were some reports of then selected for herbicide treatment, seven replicates reduced glyphosate activity. per application rate. After herbicide application all plants It is well documented that glyphosate is commonly were returned to the glasshouse and arranged in antagonized by cations and other herbicides. Nalewaja randomized blocks. Glyphosate activity was assessed by and Matysiak (1991) reported cation antagonism of measuring plant fresh weight 14 days after herbicide ap- glyphosate occurred with iron, zinc, calcium, magne- plication. sium, sodium and potassium. In contrast sulphate, phosphate, citrate and acetate anions were not antagonis- Herbicide application Herbicide was applied to plants tic and that the anions of ammonium compounds were of using a laboratory track sprayer delivering 64 L ha-1 at primary importance in overcoming glyphosate antagonis- 200 kPa via three Spraying Systems 11001 flat fan tic salts. Flint and Barrett (1989) reported antagonism of type nozzles. Nozzles were spaced 50 cm apart and 35 glyphosate by four forms of 2,4-D and two forms of cm above the plants. The boom traversed the plants at dicamba, antagonism was more significant where 6 km h-1. glyphosate was at the lower rates and 2,4-D and dicamba were at the higher rates. Hydrick and Shaw (1994) inves- Ratio experiment In the first experiment treatments tigated the effects of tank mix combinations of were trifluralin plus glyphosate as tank mix ratios of 0:1, non-selective foliar and selective soil-applied herbicides 1:2, 1:1 and 2:1. The trifluralin used was an EC (400 g on three weed species and reported antagonism was the a.i. L-1) and the glyphosate was the isopropylamine salt most frequent interaction and usually occurred when the (450 g a.i. L-1). Rates for glyphosate were 66, 105, 150, lower rates of non-selective foliar herbicides were used. 200, 300, 450, 600 and 1000 g a.i. ha-1. All treatments When the rates of non-selective herbicide were increased had Chemwet 1000® added to the tank at 0.2% spray vol- antagonism was usually overcome. Wills and McWhorter ume. (1995) reported salts of the monovalent cations ammo- nium, potassium, sodium and to a lesser degree, the anion Spray additive experiment In a second experiment four phosphate, generally resulted in increased toxicity of spray additives (Table 1) were added to the tank mix to glyphosate. test their ability to eliminate antagonism. Results from 184 Eleventh Australian Weeds Conference Proceedings the first experiment showed the greatest antagonism at a tank mix ratio of two trifluralin to one glyphosate, there- 120 fore this ratio was used in this experiment. Two tank mix 100 rates were used: trifluralin at 120 and 600 g a.i. ha-1 with 80 -1 glyphosate at 60 and 300 g a.i. ha respectively. All treat- 60 ® ments had Chemwet 1000 added at 0.2%. 40 ED 50 (g glyphosate/ha)ED 20 Experiment to measure effectiveness of Boost® A third experiment established dose response curves for 0 glyphosate, trifluralin plus glyphosate and trifluralin plus 0:1 1:2 1:1 2:1 trifluralin to glyphosate ratio glyphosate plus ammonium sulphate. Again a tank mix ratio of 2:1 trifluralin to glyphosate was used with Figure 1. Activity of glyphosate on oats applied alone glyphosate rates at 40, 60, 80, 100, 200, 400, and 800. and when tank mixed with trifluralin at 1:2, 1:1 and 2:1 Boost was added at 2% of spray volume. Chemwet 1000® glyphosate:trifluralin (error bars = 95% least significant was added to all treatments at 0.2% spray volume. intervals). Statistical analysis Non-linear regression analysis was These findings may explain why only some farmers used to fit logistic dose response curve to the data in ex- reported loss of glyphosate activity. Growers preparing periment 1 and 3 . The ED50 was calculated with a 95% paddocks for canola or legumes could have used up to least significant interval for comparison between treat- 945 g ha-1 trifluralin in the tank mix. Mixing this with the ments. highest reccommended label rate of glyphosate 450 g ha-1 gives a ratio of 2:1. If lower rates of glyphosate were RESULTS AND DISCUSSION used, the ratio would increase resulting in greater antago- Ratio experiment It was demonstrated that as the pro- nism and less activity. portion of trifluralin was increased in the tank mixture the activity of glyphosate decreased. This concurs with Spray additive experiment The addition of ammonium the findings of Hydrick and Shaw (1994) when mixing sulphate to the trifluralin glyphosate tank mix appeared imazaquin and metribuzin with glyphosate, as the pro- to eliminate the antagonism. Glyphosate applied alone portion of these chemicals increased the activity of reduced the fresh weight of oats by 96% (Table 2) when glyphosate decreased. compared to the unsprayed controls. The addition of The efficacy of glyphosate was significantly reduced trifluralin to glyphosate at a 2:1 ratio reduced the fresh in glasshouse trials when trifluralin was added to the weight of oats by 52% of the unsprayed controls. When spray tank mixture at a ratio of 1:1 or 2:1 trifluralin to ammonium sulphate was added to the tank mix the fresh glyphosate on active ingredient. The tank mix ratio of 2:1 weight of oats was reduced to 96% of the unsprayed con- reduced glyphosate activity by 46%. The 1:2 ratio treat- trols indicating a complete elimination of antagonism. ment was not significantly different from glyphosate Potassium dihydrogen orthophosphate at either concen- sprayed alone (Figure 1). tration, Flowright® and Li-700® added to the tank mix reduced oat fresh weight by 71, 37 and 47% respectively Table 1. Additives used in experiment and amounts when compared to the unsprayed controls. used for each treatment. Additive Amount Table 2. Oat fresh weight expressed as a percentage re- KH2PO4 2 parts to 1 glyphosate duction of controls. KH2PO4 4 parts to 1 glyphosate Treatment % reduction oat fresh Li-700® 345 g L-1 soyal 0.2% of spray water weight -1 phospholipids 355 g L Glyphosate 96 proponoic acid Tankmix (TM) 52 ® -1 Boost 500 g L 2% of spray water TM and KH2PO4 low rate 71 ammonium sulphate TM and KH2PO4 high rate 71 Flowright® 920 g L-1 1 part trifluralin to 3 parts TM and Li-700® 47 blend of fatty Flowright mixed together TM and Flowright® 37 triglycerides before adding to tank. TM and Boost ® 96 185 Eleventh Australian Weeds Conference Proceedings The results presented in Table 2 are treatments REFERENCES sprayed at 600 g trifluralin plus 300 g glyphosate per hec- Flint, J.L. and Barrett, M. (1989). Antagonism of tare. The lower tank mix rate treatments showed a glyphosate toxicity to Johnsongrass (Sorghum similar trend. halapensis) by 2,4-D and dicamba. Weed Science 37, 700-05. Effectiveness of ammonium sulphate experiment The Hydrick, D.E. and Shaw, D.R. (1994). Effects of tank- third experiment was carried out to verify the results ob- mix combinations of non-selective foliar and tained in the previous experiment. A complete dose re- selective soil-applied herbicides on three weed sponse curve was obtained for each treatment and the species. Weed Technology 8, 29-133. ED50 calculated for each curve. Nalewaja, J.D. and Matysiak, R. (1991). Salt antagonism The ED50 for glyphosate sprayed alone was 57 g ha-1 of glyphosate. Weed Science 39, 622-8 (Figure 3). which was significantly lower than the ED50 Nalewaja, J.D. and Matysiak, R. (1992). Species differ for trifluralin:glyphosate at 2:1 ratio which was 150 in response to adjuvants with glyphosate.
Recommended publications
  • 2,4-Dichlorophenoxyacetic Acid
    2,4-Dichlorophenoxyacetic acid 2,4-Dichlorophenoxyacetic acid IUPAC (2,4-dichlorophenoxy)acetic acid name 2,4-D Other hedonal names trinoxol Identifiers CAS [94-75-7] number SMILES OC(COC1=CC=C(Cl)C=C1Cl)=O ChemSpider 1441 ID Properties Molecular C H Cl O formula 8 6 2 3 Molar mass 221.04 g mol−1 Appearance white to yellow powder Melting point 140.5 °C (413.5 K) Boiling 160 °C (0.4 mm Hg) point Solubility in 900 mg/L (25 °C) water Related compounds Related 2,4,5-T, Dichlorprop compounds Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa) 2,4-Dichlorophenoxyacetic acid (2,4-D) is a common systemic herbicide used in the control of broadleaf weeds. It is the most widely used herbicide in the world, and the third most commonly used in North America.[1] 2,4-D is also an important synthetic auxin, often used in laboratories for plant research and as a supplement in plant cell culture media such as MS medium. History 2,4-D was developed during World War II by a British team at Rothamsted Experimental Station, under the leadership of Judah Hirsch Quastel, aiming to increase crop yields for a nation at war.[citation needed] When it was commercially released in 1946, it became the first successful selective herbicide and allowed for greatly enhanced weed control in wheat, maize (corn), rice, and similar cereal grass crop, because it only kills dicots, leaving behind monocots. Mechanism of herbicide action 2,4-D is a synthetic auxin, which is a class of plant growth regulators.
    [Show full text]
  • Exposure to Herbicides in House Dust and Risk of Childhood Acute Lymphoblastic Leukemia
    Journal of Exposure Science and Environmental Epidemiology (2013) 23, 363–370 & 2013 Nature America, Inc. All rights reserved 1559-0631/13 www.nature.com/jes ORIGINAL ARTICLE Exposure to herbicides in house dust and risk of childhood acute lymphoblastic leukemia Catherine Metayer1, Joanne S. Colt2, Patricia A. Buffler1, Helen D. Reed3, Steve Selvin1, Vonda Crouse4 and Mary H. Ward2 We examine the association between exposure to herbicides and childhood acute lymphoblastic leukemia (ALL). Dust samples were collected from homes of 269 ALL cases and 333 healthy controls (o8 years of age at diagnosis/reference date and residing in same home since diagnosis/reference date) in California, using a high-volume surface sampler or household vacuum bags. Amounts of agricultural or professional herbicides (alachlor, metolachlor, bromoxynil, bromoxynil octanoate, pebulate, butylate, prometryn, simazine, ethalfluralin, and pendimethalin) and residential herbicides (cyanazine, trifluralin, 2-methyl-4- chlorophenoxyacetic acid (MCPA), mecoprop, 2,4-dichlorophenoxyacetic acid (2,4-D), chlorthal, and dicamba) were measured. Odds ratios (OR) and 95% confidence intervals (CI) were estimated by logistic regression. Models included the herbicide of interest, age, sex, race/ethnicity, household income, year and season of dust sampling, neighborhood type, and residence type. The risk of childhood ALL was associated with dust levels of chlorthal; compared to homes with no detections, ORs for the first, second, and third tertiles were 1.49 (95% CI: 0.82–2.72), 1.49 (95% CI: 0.83–2.67), and 1.57 (95% CI: 0.90–2.73), respectively (P-value for linear trend ¼ 0.05). The magnitude of this association appeared to be higher in the presence of alachlor.
    [Show full text]
  • Sorption of Atrazine, Alachlor and Trifluralin from Water Onto Different Geosorbents
    RSC Advances Sorption of atrazine, alachlor and trifluralin from water onto different geosorbents Journal: RSC Advances Manuscript ID: RA-ART-04-2014-003886.R1 Article Type: Paper Date Submitted by the Author: 04-Dec-2014 Complete List of Authors: Leovac, Anita; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Vasyukova, Ekaterina; Technische Universität Dresden, Faculty of Environmental Sciences, Institute of Urban Water Management Ivančev-Tumbas, Ivana; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Uhl, Wolfgang; Technische Universität Dresden, Faculty of Environmental Sciences, Institute of Urban Water Management Kragulj, Marijana; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Trickovic, Jelena; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Kerkez, Đurña; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Dalmacija, Bozo; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Page 1 of 21 RSC Advances 1 Sorption of atrazine, alachlor and trifluralin from water onto different geosorbents 2 Anita S. Leovac 1, Ekaterina Vasyukova 2, Ivana I. Ivan čev-Tumbas 1, Wolfgang Uhl 2, 3 Marijana M. Kragulj 1, Jelena S. Tri čkovi ć1, Đur đa V. Kerkez 1, Božo D. Dalmacija 1
    [Show full text]
  • Trifluralin Human Health and Ecological Risk Assessment FINAL REPORT
    SERA TR-052-26-03a Trifluralin Human Health and Ecological Risk Assessment FINAL REPORT Submitted to: Paul Mistretta, COR USDA/Forest Service, Southern Region 1720 Peachtree RD, NW Atlanta, Georgia 30309 USDA Forest Service Contract: AG-3187-C-06-0010 USDA Forest Order Number: AG-43ZP-D-10-0010 SERA Internal Task No. 52-26 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 8125 Solomon Seal Manlius, New York 13104 E-Mail: [email protected] Home Page: www.sera-inc.com September 20, 2011 Table of Contents LIST OF FIGURES ...................................................................................................................... vii LIST OF TABLES ........................................................................................................................ vii LIST OF APPENDICES .............................................................................................................. viii LIST OF ATTACHEMENTS ...................................................................................................... viii ACRONYMS, ABBREVIATIONS, AND SYMBOLS ................................................................ ix COMMON UNIT CONVERSIONS AND ABBREVIATIONS .................................................. xii CONVERSION OF SCIENTIFIC NOTATION ......................................................................... xiii EXECUTIVE SUMMARY ......................................................................................................... xiv 1. INTRODUCTION .....................................................................................................................
    [Show full text]
  • Herbicide Programs for Managing Glyphosate- Resistant Palmer Amaranth and Common Waterhemp in Louisiana Corn, Cotton and Soybean
    Herbicide Programs for Managing Glyphosate- Resistant Palmer Amaranth and Common Waterhemp in Louisiana Corn, Cotton and Soybean Palmer amaranth and common waterhemp are extremely troublesome weeds in corn, cotton and soybean. They have the potential to • LOUISIANA PARISHES WITH substantially reduce crop yield and harvesting GLYPHOSATE-RESISTANCE • Red parishes efficiency. Glyphosate-resistant Palmer amaranth – Palmer amaranth and common waterhemp were documented • Orange parishes in Louisiana in 2010 and 2015, respectively. – common waterhemp Currently, Palmer amaranth has spread to essentially all crop-producing parishes in Louisiana, while glyphosate-resistant common waterhemp has only been documented in two parishes. Utilization of herbicides with differing modes of action (how they kill) for soil residual activity is vital for management of these two pigweed species. In addition, these herbicides typically need to be applied multiple times during the growing season. It is very important to control glyphosate-resistant Palmer amaranth and common waterhemp at germination or before they reach 3 inches in height. Timely applications are crucial because control with many herbicides is poor if they are applied after glyphosate-resistant Palmer amaranth height is taller than 3 inches. In addition to use of herbicides with differing modes of action, herbicide rotation in conjugation with crop rotation is a good way to avoid and/or manage glyphosate-resistant Palmer amaranth - female plant inflorescence Palmer amaranth. For example, if a corn and cotton rotation is used, herbicides with identical modes of action use in both crops should be applied sparingly. The same can be applied to corn/soybean or cotton/soybean rotations. It is important to also remember that numerous herbicides have a rotation interval restriction for a following crop.
    [Show full text]
  • Control of Crabgrass in Home Lawns
    AY-10-W IL-IN TW 33 CControlontrol ooff CrabgrassCrabgrass inin HomeHome LawnsLawns Crabgrass is a common weed that infests home lawns in the Midwest (Figure 1). Crabgrass is an summer annual weed that germinates when soil temperatures are approximately 60º F for 3-5 days at the 1/4” level. It begins fl owering and setting seed in July and dyes with the fi rst frost of fall. Crabgrass has tremendous survival reproductive Purdue University capabilities. Because of this, it is unrealistic Turf Science to expect a crabgrass free lawn. You cannot Department of eradicate crabgrass (or any other pest for that Agronomy matter); a few crabgrass plants in your lawn are Figure 1. Mature crabgrass plant (Zac Reicher). www.agry.purdue.edu/turf acceptable. Cultural Crabgrass Control The most effective way to control crabgrass is University of Illinois to create a dense, healthy turf. A healthy turf will Turfgrass Program compete well with crabgrass and prevent it from Department of establishing. Natural Mowing Resources and Environmental • Mow at 2.5 to 3.0 inches depending on the turf Sciences species. Mowing below this range will increase www.turf.uiuc.edu crabgrass populations (Figure 2). • Mow frequently so as not to remove more than Figure 2. High crabgrass population in a Kentucky 1/3 of the leaf blade at one time. This may mean bluegrass lawn mown at 1.0 inch (Aaron Patton). mowing twice weekly in spring and every other week in summer. Fertilization Irrigation Apply 2 to 4 pounds nitrogen per 1000 ft2 each Irrigate deeply and infrequently.
    [Show full text]
  • An Assessment System for Potential Groundwater Contamination From
    (continued) Extension Bulletin No. 63, March 1994 Bruce Seelig, Water Quality Specialist Trade and Common Names of Pesticides and Their Filtration Potential Herbicides ----------------------------------------------------------------- * Filtration Trade Name Common Name Potential ----------------------------------------------------------------- 2,4-D Amine 2,4-D L 2,4-D Amine 4 pound 2,4-D L 2,4-D Ester 2,4-D L 2,4-D LV Ester 2,4-D L 2,4-D LV Ester 6 2,4-D L ----------------------------------------------------------------- 2,4-D LV-4 2,4-D L 2,4-D LV-6 2,4-D L 2,4-DB 2,4-DB L 2,4-DB 1.75 2,4-DB L Aatrex4L Atrazine L ----------------------------------------------------------------- Aatrex Nine-0 Atrazine L Accent Nicosulfuron nd Accord Glyphosate H Agsco 400 2,4-D L Agsco MXL Herbicide E MCPA I ----------------------------------------------------------------- Ally Metsulfuron L Amber Triasulfuron nd Amiben Chloramben L Amine 4 2,4-D Weed Killer 2,4-D L Amitrol-T Amitrole L ----------------------------------------------------------------- Antor Diethatyl I Arena Alachlor I Ascend Bentazon L Assert Imazamethabenz L Assure II Quizalofop-P I ----------------------------------------------------------------- Atrazine Atrazine L Atrazine 4L Atrazine L Atrazine 4L Herbicide Atrazine L Atrazine 90 Atrazine L Atrazine 90 DF Atrazine L ----------------------------------------------------------------- Atrazine 90 WDG Herbicide Atrazine L Avenge Difenzoquat H Balan Benefin H Banvel Dicamba L Banvel SGF Dicamba L -----------------------------------------------------------------
    [Show full text]
  • Herbicide-Resistant Palmer Amaranth (Amaranthus Palmeri S. Wats.) in the United States — Mechanisms of Resistance, Impact, and Management
    Chapter 1 Herbicide-Resistant Palmer amaranth (Amaranthus palmeri S. Wats.) in the United States — Mechanisms of Resistance, Impact, and Management Parminder S. Chahal, Jatinder S. Aulakh, M. Jugulam and Amit J. Jhala Additional information is available at the end of the chapter http://dx.doi.org/10.5772/61512 Abstract Palmer amaranth, a dioecious summer annual species, is one of the most trouble‐ some weeds in the agronomic crop production systems in the United States. In the last two decades, continuous reliance on herbicide(s) with the same mode of action as the sole weed management strategy has resulted in the evolution of herbicide- resistant (HR) weeds, including Palmer amaranth. By 2015, Palmer amaranth bio‐ types had been confirmed resistant to acetolactate synthase (ALS)-inhibitors, dinitroanilines, glyphosate, hydroxyphenylpyruvate dioxygenase (HPPD)-inhibi‐ tors, and triazine herbicides in some parts of the United States along with multiple HR biotypes. Mechanisms of herbicide-resistance in Palmer amaranth are discussed in this chapter. Preplant herbicide options including glufosinate, 2,4-D, and dicam‐ ba provide excellent Palmer amaranth control; however, their application is limited before planting crops, which is often not possible due to unfavorable weather con‐ ditions. Agricultural biotechnology companies are developing new multiple HR crops that will allow the post-emergence application of respective herbicides for management of HR weeds, including Palmer amaranth. For the effective in-crop management of Palmer amaranth, and to reduce the potential for the evolution of other HR weeds, growers should apply herbicides with different modes of action in tank-mixture and should also incorporate cultural practices including inversion till‐ age and cover crops along with herbicide programs.
    [Show full text]
  • Using Countless Tons of Arsenic As a Non-Selective Contact and Soil Sterilant
    87 In addition to requiring the user to obtain a permit from, the agricultural commissioner, t4e regulations prescribe certain conditions to be met by those who possess or use sodium arsenite as follows: (a) No pesticide containing sodium arsenite shall be applied on exposed vegetation (other than dormant grapeviries) unless the vegetation to be treated is enclosed within a good and su£ficient fence or otherwis.e made inaccessible to grazing animals, pets, and children. (b) No pesticide containing sodium arsenite sha,11 be applied on soil or vegetation (other than dormant grapevines) in any area penetrated by roots of any plant of value, without the written consent of the owner of such plant. ( c) No pesticide containing sodium arsenite shall be kept or placed in drinking cups, pop bottles, or other containers of a type commonly used for food or drink. (d) No pesticide containing sodium arsenite, whether in concentrated or dilute form, shall be stored, placed, or transported in any container or receptacle which does not bear on the outside a conspicuous poison label which conforms to the label required to be placed on all packages of arsenic compounds and pre:parations sold or delivered within the State. These are only procedures that any careful person would observe in the use of a poisonous material like sodium arsenite. It is just over one year since the regulations became effective. In that time we have heard of no accidental deaths involving sodium arsenite in California and the regulations appear to be serving a good purpose. SUBSTITUTE HERBICIDES FOR SODIUM ARSENITE W.
    [Show full text]
  • Revised Reregistration Eligibility Decision for MSMA, DSMA, CAMA
    Revised Reregistration Eligibility Decision for MSMA, DSMA, CAMA, and Cacodylic Acid August 10, 2006 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C. 20460 OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES MEMORANDUM Date: August 10, 2006 Subject: Revised “Reregistration Eligibility Decision for MSMA, DSMA, CAMA, and Cacodylic Acid” Document From: Lance Wormell, Chemical Review Manager Reregistration Branch 2 Special Review and Reregistration Division To: Organic Arsenical Herbicides Docket (EPA-HQ-OPP-2006-0201) EPA originally published the “Reregistration Eligibility Decision for MSMA, DSMA, CAMA, and Cacodylic Acid” (EPA 738-R-06-021) in the electronic docket on August 9, 2006. EPA has since identified and corrected a typographical error on page 22. The cancer slope factor for inorganic arsenic used to calculate the exposure level in drinking water was incorrectly listed as 3.67 x 10-3 (mg/kg/day)-1. The value has since been corrected to 3.67 (mg/kg/day)-1. The typographical change in the document does not alter EPA’s calculations or conclusions and the current document should be used in place of the previous version. United States Office of Prevention, Pesticides EPA 738-R-06-021 Environmental Protection And Toxic Substances July 2006 Agency (7508P) _________________________________________________________________ Reregistration Eligibility Decision for MSMA, DSMA, CAMA, and Cacodylic Acid List B Case Nos. 2395, 2080 TABLE OF CONTENTS I. Introduction.............................................................................................................
    [Show full text]
  • 3425Laybyweedcontrolinsugar
    Louisiana Field Crops IPM Information for Identifying and Controlling Diseases, Insects and Weeds Layby Weed Control in Sugarcane Layby herbicides for sugarcane are applied broadcast and directed un- derneath the sugarcane canopy, usually following the last cultivation (Figures 1 and 2). It is necessary that the lower canopy be contacted by the spray solu- tion to ensure weed control both in the sugarcane drill and in the row middle. If weeds are present, nonionic surfac- tant at 1 to 2 quarts per 100 gallons of solution or crop oil concentrate at 2 to 4 quarts per 100 gallons should be added to the spray solution for herbi- cides with postemergence activity. Layby is an important time to Figure 1. Broadcast application of herbicide in May at layby using two control itchgrass (Raoulgrass), seedling nozzles per row middle. johnsongrass, browntop millet and other annual grasses. Preemergence herbicide options for controlling grasses include the herbicides Pendi- 72-inch Nozzle Spacing methalin/Prowl H2O/others and Tre- flan/Trifluralin/others. Due to the rapid decomposition of Pendimethalin/Prowl H2O/others by sunlight, rainfall of a half-inch is required within seven to 10 days of application. Treflan/Trifluralin/ others is subject to volatility and must be incorporated within 24 hours after application. Since row middles are worked at layby, some growers prefer to incorporate a trifluralin product at the same time. This is an economical 72-inch treatment and incorporation helps to Row Spacing ensure the herbicide is in the soil when weed seeds begin to germinate. Figure 2. Broadcast application of herbicide at layby.
    [Show full text]
  • Environmental Fate of TCDD and Agent Orange and Bioavailability to Troops in Vietnam
    DIOXIN IN VIETNAM: CHARACTERISATION, MONITORING, REMEDIATION AND EFFECTS Environmental Fate of TCDD and Agent Orange and Bioavailability to Troops in Vietnam Nathan J. Karch1, Deborah K. Watkins1, Alvin L. Young2, Michael E. Ginevan1 ''Exponent, Inc., Washington, DC, USA 2University of Oklahoma, Norman, Oklahoma, USA Introduction This paper reviews the environmental fate of Agent Orange and the contaminant, 2,3,7,8- tetrachlorodibenzo-p-dioxin (TCDD), and discusses how this affects the bioavailability of TCDD for ground troops in Vietnam. Methods and Materials From 1962 to 1971, herbicides were sprayed in Vietnam to defoliate the jungle canopy and to destroy crops, exposing the enemy and denying them food, and to clear tall grasses and bushes from the perimeters of US base camps and outlying fire-support bases. The most widely used herbicides were phenoxyacetic acids - 2,4-dichlorophenoxyacetic acid (2,4-D), 2,4,5- trichlorophenoxyacetic acid (2,4,5-T), picloram and cacodylic acid. Only the herbicides containing 2,4,5-T were contaminated with TCDD - Agents Orange, Green, Pink and Purple. Dispersion of Agent Orange: The US Air Force was responsible for training aircrews, developing aerial tactics for herbicide missions and the developing, testing and evaluating spray equipment. These programs were conducted mainly at Eglin Air Force Base, Florida and to a lesser degree at Pran Buri Calibration Grid in Thailand. Responsibility for the defoliant rested with the US Army at Fort Detrick, Maryland with the cooperation of the US Department of Agriculture.1, 2 Extensive field tests with herbicide determined optimum conditions and deposition rate for Vietnam. Dispersal of herbicide droplets by air turbulence could be minimized by scheduling missions in favorable weather conditions and by controlling droplet size.
    [Show full text]